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Fachin PA, Thomaz EL, Fernandes NF, Coelho Netto AL. Seven decades of Atlantic rainforest conversion to slash-and-burn agriculture: Effects on soil's physical properties. JOURNAL OF ENVIRONMENTAL MANAGEMENT 2024; 350:119682. [PMID: 38039705 DOI: 10.1016/j.jenvman.2023.119682] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Key Words] [Track Full Text] [Subscribe] [Scholar Register] [Received: 05/24/2023] [Revised: 10/27/2023] [Accepted: 11/10/2023] [Indexed: 12/03/2023]
Abstract
Slash-and-burn agriculture is a millennia-old no-till farming technique that is still widely practiced in developing tropical countries. This practice is currently employed in Brazil by subsistence family farms, Indigenous groups, and maroons, in a primitive manner, using only cutting, fire, and fallow as soil preparation techniques for food production. In recent years, this practice has been drastically reduced. However, the fallow periods have become even shorter. Therefore, there is a need to understand how the recurrence of fire with the reduction of fallow time affects the soil. This study aims to evaluate the cumulative effects of fire recurrence in slash-and-burn agriculture for seven decades on the physical properties of the soil and the minimum fallow times for post-burn resilience. Using a chronosequence approach, different fallow periods: a) native forest (control); b) recently burned (30 days after fire); c) 2-year fallow; d) 5-year fallow; e) 7-year fallow; f) 12-year fallow were considered. In each area, six disturbed and six undisturbed samples were randomly collected at 0-5 cm and 5-10 cm depths each to estimate: soil bulk density, soil total porosity, penetration resistance, aggregate stability, mean weight diameter, and soil water retention capacity. The results show that the seven decades of slash-and-burn agriculture affected the topsoil (0-5 cm deep) more prominently. Curiously, soil bulk density and total porosity were not affected at any time between the areas. The fire increased penetration resistance immediately after burning in the 0-5 cm layer by 162.5%, showing resilience after five years of fallow. Soil aggregate stability showed a delayed effect, with a significant increase in two years after the fire by 64.2%, remaining high after 12 years of fallow, indicating the influence of other mechanisms and reactions in the soil after the fire. The mean weight diameter did not change at any time while soil water retention increased immediately after burning by 25.2% with resilience after a two-year fallow. Most physical properties were not directly affected by fire heating but by post-fire environmental conditions and the interaction of various mechanisms during the fallow period. In general, most physical parameters showed good resilience over an average of five years of fallow, with cumulative effects only for aggregate stability.
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Affiliation(s)
- Paulo Angelo Fachin
- Soil Erosion Laboratory, Department of Geography, Universidade Estadual do Centro-Oeste, UNICENTRO, Street Simeão Camargo Varela de Sá, 03 Caixa Postal 3010, 85040-080, Guarapuava, Paraná, Brazil; Pedo-geomophological Monitoring and Modeling Laboratory, Department of Geography, Universidade Federal do Rio de Janeiro, UFRJ, Street Athos da Silveira Ramos, 274, CEP 21941-916, Cidade Universitária, Ilha do Fundão, Rio de Janeiro, RJ, Brazil; Geohydrology Laboratory, Department of Geography, Universidade Federal do Rio de Janeiro, UFRJ, Street Athos da Silveira Ramos, 274, CEP 21941-916, Cidade Universitária, Ilha do Fundão, Rio de Janeiro, RJ, Brazil.
| | - Edivaldo Lopes Thomaz
- Soil Erosion Laboratory, Department of Geography, Universidade Estadual do Centro-Oeste, UNICENTRO, Street Simeão Camargo Varela de Sá, 03 Caixa Postal 3010, 85040-080, Guarapuava, Paraná, Brazil
| | - Nelson Ferreira Fernandes
- Pedo-geomophological Monitoring and Modeling Laboratory, Department of Geography, Universidade Federal do Rio de Janeiro, UFRJ, Street Athos da Silveira Ramos, 274, CEP 21941-916, Cidade Universitária, Ilha do Fundão, Rio de Janeiro, RJ, Brazil
| | - Ana Luiza Coelho Netto
- Geohydrology Laboratory, Department of Geography, Universidade Federal do Rio de Janeiro, UFRJ, Street Athos da Silveira Ramos, 274, CEP 21941-916, Cidade Universitária, Ilha do Fundão, Rio de Janeiro, RJ, Brazil
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Hyperspectral Inversion of Soil Carbon and Nutrient Contents in the Yellow River Delta Wetland. DIVERSITY 2022. [DOI: 10.3390/d14100862] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [Abstract] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 11/07/2022]
Abstract
Hyperspectral inversion techniques can facilitate soil quality monitoring and evaluation. In this study, the Yellow River Delta Wetland Nature Reserve was used as the study area. By measuring and analyzing soil samples under different vegetation types and collecting soil reflectance spectra, the relationships between vegetation types, soil depth, and the changes in soil total carbon (TC), total nitrogen (TN), and total phosphorus (TP) contents were assessed. The spectral data set was changed by spectral first derivative processing and division of the sample set according to vegetation type. The correlation between soil carbon, nitrogen, and phosphorus contents, and soil spectra was also analyzed, sensitive bands were selected, and the partial least-squares (PLS) method, support vector machine (SVM) method, and random forest (RF) model were used to establish the inversion model based on the characteristic bands. The optimal combination of spectral transformation, sample set partitioning, and inversion model was explored. The results showed significant differences (p < 0.05) in soil TC, TN, and TP contents under reed and saline alkali poncho vegetation, but not between soil element contents under different stratifications of the same plant species. The first derivative reflectance had higher correlation coefficients with soil TC, TN, and TP contents compared with the original reflectance, while the sensitive bands and quantities of the three elements differed. The division of the sample sets according to vegetation type and the first derivative treatment can improve the prediction accuracy of the model. The best combination of sample set plus FD plus RF for TC, TN, and TP in reed soil and sample set plus FD plus SVM for TC, TN, and TP in saline alkali pine soil provides technical support to further improve the prediction accuracy of TC, TN, and TP in wetland soil.
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